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Shark Depredation and Unwanted Bycatch in Pelagic Longline

Shark Depredation and Unwanted Bycatch in Pelagic Longline

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Potential of Deterrents, Hotspot Avoidance <strong>and</strong> Incentive Instruments to Reduce <strong>Shark</strong> Interactions <strong>in</strong> <strong>Pelagic</strong> Longl<strong>in</strong>e Fisheries<br />

The Commission for the Conservation of Antarctic Mar<strong>in</strong>e Liv<strong>in</strong>g<br />

Resources has made some prelim<strong>in</strong>ary progress towards establish<strong>in</strong>g<br />

a system of mar<strong>in</strong>e protected areas <strong>in</strong> the Southern Ocean.<br />

Consequences of establish<strong>in</strong>g a protected area need to be carefully<br />

considered, as resource use restrictions of a mar<strong>in</strong>e protected area<br />

may displace effort to adjacent <strong>and</strong> potentially more sensitive <strong>and</strong><br />

valuable areas, where weaker management frameworks may be <strong>in</strong><br />

place (Murray et al., 2000; Baum et al., 2003; Kotas et al., 2004). Also,<br />

measures adopted by regional fishery management organizations<br />

<strong>and</strong> other <strong>in</strong>ternational bodies are only b<strong>in</strong>d<strong>in</strong>g to parties to the<br />

Convention that established the organization, <strong>and</strong> will not control<br />

activities by non-party States. Thus, another consideration for<br />

employ<strong>in</strong>g high seas mar<strong>in</strong>e protected areas to manage problematic<br />

fisheries bycatch is that clos<strong>in</strong>g areas to fisheries only of party States<br />

could result <strong>in</strong> <strong>in</strong>creased effort <strong>in</strong> this area by fleets from non-party<br />

States with fewer or no controls to manage bycatch, exacerbat<strong>in</strong>g the<br />

problem for which the MPA was established to address.<br />

International bodies have created mar<strong>in</strong>e protected areas on the high<br />

seas: The International Whal<strong>in</strong>g Commission declared the Indian<br />

<strong>and</strong> Southern Oceans as no-take sanctuaries for whales, cover<strong>in</strong>g 30<br />

percent of the world’s oceans mostly on the high seas. Conventions<br />

govern<strong>in</strong>g <strong>in</strong>ternational shipp<strong>in</strong>g have designated large areas of<br />

the ocean that <strong>in</strong>clude high seas as Special Areas where str<strong>in</strong>gent<br />

restrictions apply regard<strong>in</strong>g discharges from ships. Furthermore,<br />

under the United Nations Convention on the Law of the Sea, the<br />

International Seabed Authority could protect areas from m<strong>in</strong>erals<br />

extraction beyond national jurisdiction where there is a risk of harm<br />

to the mar<strong>in</strong>e environment (Kelleher, 1999). Recent developments<br />

with<strong>in</strong> the framework of the United Nations Convention on the Law<br />

of the Sea <strong>and</strong> associated conventions may make it possible <strong>in</strong> the<br />

future to restrict fisheries activities on the high seas that are shown<br />

to underm<strong>in</strong>e mar<strong>in</strong>e conservation (Kelleher, 1999).<br />

7.3. Incentive Instruments<br />

Several <strong>in</strong>centive <strong>in</strong>struments can be <strong>in</strong>stituted by <strong>in</strong>dustry,<br />

management authorities, <strong>and</strong> conservation groups to contribute to<br />

<strong>in</strong>dustry employment of methods to reduce shark bycatch <strong>and</strong> <strong>in</strong>jury<br />

(Gilman et al., 2002).<br />

7.3.1. National <strong>and</strong> local constra<strong>in</strong>ts<br />

National-level legal, regulatory, <strong>and</strong> policy-derived formal constra<strong>in</strong>ts,<br />

comb<strong>in</strong>ed with an effective surveillance <strong>and</strong> enforcement program,<br />

can promote fish<strong>in</strong>g <strong>in</strong>dustry compliance with laws, rules, <strong>and</strong> policies<br />

to m<strong>in</strong>imize shark bycatch. For <strong>in</strong>stance, restrictions on shark f<strong>in</strong>n<strong>in</strong>g,<br />

wire trace <strong>and</strong> per trip shark retention are examples of regulatory<br />

constra<strong>in</strong>ts on pelagic longl<strong>in</strong>e fishery <strong>in</strong>teractions with sharks.<br />

Time/are closures <strong>and</strong> m<strong>and</strong>atory use of avoidance techniques (e.g.,<br />

proscrib<strong>in</strong>g a m<strong>in</strong>imum depth for the sett<strong>in</strong>g of baited hooks through<br />

certa<strong>in</strong> gear design specifications, us<strong>in</strong>g fish <strong>in</strong>stead of squid for<br />

bait, prohibit<strong>in</strong>g use of light sticks) are other examples of potential<br />

regulatory tools to manage shark bycatch <strong>and</strong> depredation (Hall et<br />

al., 2000; Gilman et al., 2005). Fishery management authorities could<br />

create a fee <strong>and</strong> exemption structure for shark bycatch, applicable<br />

to <strong>in</strong>dividual vessels or to an entire fleet, similar to a “polluter pays”<br />

system. Alternatively, the fee structure could provide a positive<br />

reward-based <strong>in</strong>centive, where a higher subsidy, lower permit or<br />

license fee, earlier start to the fish<strong>in</strong>g season, or lower taxes apply, <strong>and</strong><br />

a positive image is portrayed when a vessel or fleet meets st<strong>and</strong>ards for<br />

shark bycatch. The threat of a fishery closure if performance st<strong>and</strong>ards<br />

related to shark <strong>in</strong>teractions are not met provides a strong <strong>in</strong>centive for<br />

<strong>in</strong>dustry compliance to m<strong>in</strong>imize shark <strong>in</strong>teractions.<br />

7.3.2. Regional <strong>and</strong> <strong>in</strong>ternational accords, regulations, <strong>and</strong><br />

policies<br />

Multilateral treaties <strong>and</strong> accords that address shark <strong>in</strong>teractions can<br />

obligate national governments to adopt enabl<strong>in</strong>g legislation to manage<br />

these <strong>in</strong>teractions. Regional Fishery Management Organizations can<br />

adopt regulations <strong>and</strong> policies to manage <strong>in</strong>teractions between fisheries<br />

<strong>and</strong> sensitive species for compliance by member nations. Multilateral<br />

bodies can adopt advisory policies to encourage fish<strong>in</strong>g nations to<br />

susta<strong>in</strong>ably manage shark-longl<strong>in</strong>e <strong>in</strong>teractions. Recent <strong>in</strong>ternational<br />

<strong>in</strong>itiatives address<strong>in</strong>g shark f<strong>in</strong>n<strong>in</strong>g are summarized <strong>in</strong> the Introduction.<br />

7.3.3. Eco-label<strong>in</strong>g<br />

Consumer dem<strong>and</strong> can alter <strong>in</strong>dustry behavior. In 2005 the Committee<br />

on Fisheries of the Food <strong>and</strong> Agriculture Organization of the United<br />

Nations adopted Guidel<strong>in</strong>es for the Ecolabell<strong>in</strong>g of Fish <strong>and</strong> Fishery<br />

Products from Mar<strong>in</strong>e Capture Fisheries. The new guidel<strong>in</strong>es provide<br />

guidance to governments <strong>and</strong> organizations that already ma<strong>in</strong>ta<strong>in</strong>, or are<br />

consider<strong>in</strong>g establish<strong>in</strong>g, label<strong>in</strong>g schemes for certify<strong>in</strong>g <strong>and</strong> promot<strong>in</strong>g<br />

labels for fish <strong>and</strong> fishery products from well-managed mar<strong>in</strong>e capture<br />

fisheries. A longl<strong>in</strong>e fish<strong>in</strong>g <strong>in</strong>dustry can pursue certification or<br />

accreditation from an eco-label<strong>in</strong>g certification program, <strong>in</strong> part, to<br />

demonstrate the employment of best practices to reduce shark bycatch<br />

<strong>and</strong> discards. The <strong>in</strong>centives to <strong>in</strong>dustry are market-based, to <strong>in</strong>crease<br />

dem<strong>and</strong> for <strong>and</strong> value of their products, <strong>and</strong> social, to receive recognition<br />

from the public for comply<strong>in</strong>g with accepted norms (Wessells et al.,<br />

1999). Eco-label<strong>in</strong>g can serve as an effective market<strong>in</strong>g tool for a fish<strong>in</strong>g<br />

<strong>in</strong>dustry, when properly managed. For <strong>in</strong>stance, certification under an<br />

eco-label<strong>in</strong>g scheme can be used as a market<strong>in</strong>g tool to develop <strong>and</strong><br />

market an image <strong>and</strong> product differentiation, through advertis<strong>in</strong>g, sales<br />

promotion, public relations, direct market<strong>in</strong>g, <strong>and</strong> media coverage.<br />

A company can differentiate their products from other seafood as<br />

orig<strong>in</strong>at<strong>in</strong>g from a fishery that follows <strong>in</strong>ternationally accepted practices<br />

to ensure environmental susta<strong>in</strong>ability. This is a form of cause-related<br />

market<strong>in</strong>g, a proven means to promote recognition <strong>and</strong> develop a<br />

positive company image <strong>and</strong> reputation.<br />

7.3.4. Industry <strong>and</strong> market self-polic<strong>in</strong>g<br />

A longl<strong>in</strong>e <strong>in</strong>dustry can create a program where <strong>in</strong>formation on<br />

<strong>in</strong>dividual vessel shark bycatch levels <strong>and</strong> compliance with relevant<br />

regulations is made available to the entire <strong>in</strong>dustry. This self-polic<strong>in</strong>g<br />

program uses peer pressure with<strong>in</strong> the fish<strong>in</strong>g <strong>in</strong>dustry to criticize<br />

‘bad actors’ <strong>and</strong> publicly acknowledge those fishers who are operat<strong>in</strong>g<br />

<strong>in</strong> a responsible manner. For example, the North Pacific Longl<strong>in</strong>e<br />

Association <strong>in</strong>itiated a seabird bycatch report card system among<br />

its members <strong>in</strong> 2000 (Fitzgerald et al. 2004). Also, there are market<br />

pressures to avoid br<strong>in</strong>g<strong>in</strong>g <strong>in</strong> target species damaged by sharks.<br />

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